Abstract

Abstract. During the last decades an increasing area of drained peatlands has been rewetted. Especially in Germany, rewetting is the principal treatment on cutover sites when peat extraction is finished. The objectives are bog restoration and the reduction of greenhouse gas (GHG) emissions. The first sites were rewetted in the 1980s. Thus, there is a good opportunity to study long-term effects of rewetting on greenhouse gas exchange, which has not been done so far on temperate cutover peatlands. Moreover, Sphagnum cultivating may become a new way to use cutover peatlands and agriculturally used peatlands as it permits the economical use of bogs under wet conditions. The climate impact of such measures has not been studied yet. We conducted a field study on the exchange of carbon dioxide, methane and nitrous oxide at three rewetted sites with a gradient from dry to wet conditions and at a Sphagnum cultivation site in NW Germany over the course of more than 2 years. Gas fluxes were measured using transparent and opaque closed chambers. The ecosystem respiration (CO2) and the net ecosystem exchange (CO2) were modelled at a high temporal resolution. Measured and modelled values fit very well together. Annually cumulated gas flux rates, net ecosystem carbon balances (NECB) and global warming potential (GWP) balances were determined. The annual net ecosystem exchange (CO2) varied strongly at the rewetted sites (from −201.7 ± 126.8 to 29.7± 112.7g CO2-C m−2 a−1) due to differing weather conditions, water levels and vegetation. The Sphagnum cultivation site was a sink of CO2 (−118.8 ± 48.1 and −78.6 ± 39.8 g CO2-C m−2 a−1). The annual CH4 balances ranged between 16.2 ± 2.2 and 24.2 ± 5.0g CH4-C m−2 a−1 at two inundated sites, while one rewetted site with a comparatively low water level and the Sphagnum farming site show CH4 fluxes close to 0. The net N2O fluxes were low and not significantly different between the four sites. The annual NECB was between −185.5 ± 126.9 and 49.9 ± 112.8 g CO2-C m−2 a−1 at the rewetted sites and −115.8 ± 48.1 and −77 ± 39.8 g CO2-C m−2 a−1 at the Sphagnum cultivating site. The annual GWP100 balances ranged from −280.5 ± 465.2 to 644.5 ± 413.6 g CO2-eq. m−2 a−1 at the rewetted sites. In contrast, the Sphagnum farming site had a cooling impact on the climate in both years (−356.8 ± 176.5 and −234.9 ± 145.9 g CO2-C m−2 a−1). If the carbon exported through the harvest of the Sphagnum biomass and the additional CO2 emission from the decay of the organic material is considered, the NECB and GWP100 balances are near neutral. Peat mining sites are likely to become net carbon sinks and a peat accumulating ("growing") peatland within 30 years of rewetting, but the GWP100 balance may still be positive. A recommended measure for rewetting is to achieve a water level of a few centimetres below ground. Sphagnum farming is a climate-friendly alternative to conventional commercial use of bogs. A year-round constant water level of a few centimetres below ground level should be maintained.

Highlights

  • Over many centuries, peatlands have been drained and used for peat extraction, agriculture and forestry worldwide and, in particular, in Germany (Couwenberg, 2011)

  • Temperatures and photosynthetic active radiation (PAR) were used for the modelling during each measurement campaign, while other controls, such as soil moisture or vegetation, were not considered in the short term but only in the long term, regardless of the fact that these may change over the course of the day

  • Factors having an effect in the long term are accounted for by the repeated measurement campaigns, which result in different model parameters as a consequence of the different field situations

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Summary

Introduction

Peatlands have been drained and used for peat extraction, agriculture and forestry worldwide and, in particular, in Germany (Couwenberg, 2011). Peat has been extracted by industrial means on more than 30 000 ha in northwest Germany, and since the mid 1980s rewetting and restoration is obligatory on abandoned. In the long term, rewetting and restoration of the former cutover sites aims at establishing vegetation which is typical for growing, peat-accumulating bogs. In the short term, flooding may lead to high methane emissions, depending on the water level and the time of year when flooding takes place (Waddington and Roulet, 1996; Le Mer and Roger, 2001; Houghton, 2004). In the intermediate and long term, methane emissions are supposed to decrease and peat accumulation will lead to CO2 uptake at the site (Augustin and Joosten, 2007). Little is known about the time dependency of these processes under temperate conditions and the total balance of the greenhouse gases

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